NO346496B1 - A method and arrangement for capturing CO2 - Google Patents
A method and arrangement for capturing CO2 Download PDFInfo
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- NO346496B1 NO346496B1 NO20200431A NO20200431A NO346496B1 NO 346496 B1 NO346496 B1 NO 346496B1 NO 20200431 A NO20200431 A NO 20200431A NO 20200431 A NO20200431 A NO 20200431A NO 346496 B1 NO346496 B1 NO 346496B1
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- adsorbent bed
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- 238000000034 method Methods 0.000 title claims description 34
- 239000003570 air Substances 0.000 claims description 174
- 239000003463 adsorbent Substances 0.000 claims description 137
- 238000005338 heat storage Methods 0.000 claims description 46
- 239000002274 desiccant Substances 0.000 claims description 45
- 239000007789 gas Substances 0.000 claims description 43
- 238000001179 sorption measurement Methods 0.000 claims description 39
- 238000003795 desorption Methods 0.000 claims description 23
- 238000010438 heat treatment Methods 0.000 claims description 20
- 239000011324 bead Substances 0.000 claims description 15
- 239000010457 zeolite Substances 0.000 claims description 12
- 239000003546 flue gas Substances 0.000 claims description 9
- 239000012080 ambient air Substances 0.000 claims description 8
- 238000012546 transfer Methods 0.000 claims description 8
- 239000011232 storage material Substances 0.000 claims description 5
- 239000000919 ceramic Substances 0.000 claims description 4
- 230000004087 circulation Effects 0.000 claims description 4
- 229910052751 metal Inorganic materials 0.000 claims description 4
- 239000002184 metal Substances 0.000 claims description 4
- 238000011084 recovery Methods 0.000 claims 14
- 239000000112 cooling gas Substances 0.000 claims 2
- 238000001035 drying Methods 0.000 claims 2
- 239000000463 material Substances 0.000 claims 2
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 47
- 230000007704 transition Effects 0.000 description 25
- 238000001816 cooling Methods 0.000 description 23
- 230000008569 process Effects 0.000 description 22
- 230000008929 regeneration Effects 0.000 description 22
- 238000011069 regeneration method Methods 0.000 description 22
- 238000003860 storage Methods 0.000 description 16
- 241000196324 Embryophyta Species 0.000 description 9
- 230000018044 dehydration Effects 0.000 description 8
- 238000006297 dehydration reaction Methods 0.000 description 8
- 230000005068 transpiration Effects 0.000 description 8
- 239000000126 substance Substances 0.000 description 7
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 description 6
- 229910021536 Zeolite Inorganic materials 0.000 description 6
- 238000010586 diagram Methods 0.000 description 6
- HNPSIPDUKPIQMN-UHFFFAOYSA-N dioxosilane;oxo(oxoalumanyloxy)alumane Chemical compound O=[Si]=O.O=[Al]O[Al]=O HNPSIPDUKPIQMN-UHFFFAOYSA-N 0.000 description 6
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 description 5
- 229910002027 silica gel Inorganic materials 0.000 description 5
- 239000000741 silica gel Substances 0.000 description 5
- KWYUFKZDYYNOTN-UHFFFAOYSA-M Potassium hydroxide Chemical compound [OH-].[K+] KWYUFKZDYYNOTN-UHFFFAOYSA-M 0.000 description 4
- 230000015556 catabolic process Effects 0.000 description 4
- 238000006731 degradation reaction Methods 0.000 description 4
- 238000013461 design Methods 0.000 description 4
- 238000005265 energy consumption Methods 0.000 description 4
- 238000005516 engineering process Methods 0.000 description 4
- 239000000203 mixture Substances 0.000 description 4
- 230000008635 plant growth Effects 0.000 description 4
- 235000013311 vegetables Nutrition 0.000 description 4
- 150000001412 amines Chemical class 0.000 description 3
- 230000008901 benefit Effects 0.000 description 3
- 238000011161 development Methods 0.000 description 3
- 230000018109 developmental process Effects 0.000 description 3
- 230000000694 effects Effects 0.000 description 3
- 230000005855 radiation Effects 0.000 description 3
- 239000007787 solid Substances 0.000 description 3
- 238000009834 vaporization Methods 0.000 description 3
- 230000008016 vaporization Effects 0.000 description 3
- PNEYBMLMFCGWSK-UHFFFAOYSA-N aluminium oxide Inorganic materials [O-2].[O-2].[O-2].[Al+3].[Al+3] PNEYBMLMFCGWSK-UHFFFAOYSA-N 0.000 description 2
- -1 amine compounds Chemical class 0.000 description 2
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 2
- 230000000711 cancerogenic effect Effects 0.000 description 2
- 231100000315 carcinogenic Toxicity 0.000 description 2
- 238000002485 combustion reaction Methods 0.000 description 2
- 150000001875 compounds Chemical class 0.000 description 2
- 239000002826 coolant Substances 0.000 description 2
- 238000004134 energy conservation Methods 0.000 description 2
- 239000007788 liquid Substances 0.000 description 2
- 238000011068 loading method Methods 0.000 description 2
- 239000001301 oxygen Substances 0.000 description 2
- 229910052760 oxygen Inorganic materials 0.000 description 2
- 238000005192 partition Methods 0.000 description 2
- BWHMMNNQKKPAPP-UHFFFAOYSA-L potassium carbonate Chemical compound [K+].[K+].[O-]C([O-])=O BWHMMNNQKKPAPP-UHFFFAOYSA-L 0.000 description 2
- 238000002203 pretreatment Methods 0.000 description 2
- 239000000047 product Substances 0.000 description 2
- 239000002594 sorbent Substances 0.000 description 2
- 208000031888 Mycoses Diseases 0.000 description 1
- 239000004411 aluminium Substances 0.000 description 1
- XAGFODPZIPBFFR-UHFFFAOYSA-N aluminium Chemical compound [Al] XAGFODPZIPBFFR-UHFFFAOYSA-N 0.000 description 1
- 230000008859 change Effects 0.000 description 1
- 239000000356 contaminant Substances 0.000 description 1
- 238000007791 dehumidification Methods 0.000 description 1
- 230000001419 dependent effect Effects 0.000 description 1
- 230000009977 dual effect Effects 0.000 description 1
- 238000005243 fluidization Methods 0.000 description 1
- 230000012010 growth Effects 0.000 description 1
- XLYOFNOQVPJJNP-UHFFFAOYSA-M hydroxide Chemical compound [OH-] XLYOFNOQVPJJNP-UHFFFAOYSA-M 0.000 description 1
- 239000003621 irrigation water Substances 0.000 description 1
- 230000007774 longterm Effects 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 238000002156 mixing Methods 0.000 description 1
- 230000004048 modification Effects 0.000 description 1
- 238000012986 modification Methods 0.000 description 1
- 150000004005 nitrosamines Chemical class 0.000 description 1
- 231100000614 poison Toxicity 0.000 description 1
- 229910000027 potassium carbonate Inorganic materials 0.000 description 1
- 239000002244 precipitate Substances 0.000 description 1
- 238000001556 precipitation Methods 0.000 description 1
- 239000011435 rock Substances 0.000 description 1
- 229920006395 saturated elastomer Polymers 0.000 description 1
- 230000035945 sensitivity Effects 0.000 description 1
- LIVNPJMFVYWSIS-UHFFFAOYSA-N silicon monoxide Chemical class [Si-]#[O+] LIVNPJMFVYWSIS-UHFFFAOYSA-N 0.000 description 1
- 229910052814 silicon oxide Inorganic materials 0.000 description 1
- 231100000331 toxic Toxicity 0.000 description 1
- 230000002588 toxic effect Effects 0.000 description 1
- 239000003440 toxic substance Substances 0.000 description 1
- 238000011144 upstream manufacturing Methods 0.000 description 1
Classifications
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/02—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by adsorption, e.g. preparative gas chromatography
- B01D53/06—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by adsorption, e.g. preparative gas chromatography with moving adsorbents, e.g. rotating beds
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/02—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by adsorption, e.g. preparative gas chromatography
- B01D53/04—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by adsorption, e.g. preparative gas chromatography with stationary adsorbents
- B01D53/0407—Constructional details of adsorbing systems
- B01D53/0438—Cooling or heating systems
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/02—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by adsorption, e.g. preparative gas chromatography
- B01D53/04—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by adsorption, e.g. preparative gas chromatography with stationary adsorbents
- B01D53/0407—Constructional details of adsorbing systems
- B01D53/0446—Means for feeding or distributing gases
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/02—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by adsorption, e.g. preparative gas chromatography
- B01D53/04—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by adsorption, e.g. preparative gas chromatography with stationary adsorbents
- B01D53/0462—Temperature swing adsorption
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/14—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by absorption
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/26—Drying gases or vapours
- B01D53/261—Drying gases or vapours by adsorption
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F24—HEATING; RANGES; VENTILATING
- F24F—AIR-CONDITIONING; AIR-HUMIDIFICATION; VENTILATION; USE OF AIR CURRENTS FOR SCREENING
- F24F3/00—Air-conditioning systems in which conditioned primary air is supplied from one or more central stations to distributing units in the rooms or spaces where it may receive secondary treatment; Apparatus specially designed for such systems
- F24F3/12—Air-conditioning systems in which conditioned primary air is supplied from one or more central stations to distributing units in the rooms or spaces where it may receive secondary treatment; Apparatus specially designed for such systems characterised by the treatment of the air otherwise than by heating and cooling
- F24F3/14—Air-conditioning systems in which conditioned primary air is supplied from one or more central stations to distributing units in the rooms or spaces where it may receive secondary treatment; Apparatus specially designed for such systems characterised by the treatment of the air otherwise than by heating and cooling by humidification; by dehumidification
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2253/00—Adsorbents used in seperation treatment of gases and vapours
- B01D2253/10—Inorganic adsorbents
- B01D2253/106—Silica or silicates
- B01D2253/108—Zeolites
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2257/00—Components to be removed
- B01D2257/50—Carbon oxides
- B01D2257/504—Carbon dioxide
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2257/00—Components to be removed
- B01D2257/80—Water
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2258/00—Sources of waste gases
- B01D2258/02—Other waste gases
- B01D2258/0283—Flue gases
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2258/00—Sources of waste gases
- B01D2258/06—Polluted air
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2259/00—Type of treatment
- B01D2259/65—Employing advanced heat integration, e.g. Pinch technology
- B01D2259/655—Employing advanced heat integration, e.g. Pinch technology using heat storage materials
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02C—CAPTURE, STORAGE, SEQUESTRATION OR DISPOSAL OF GREENHOUSE GASES [GHG]
- Y02C20/00—Capture or disposal of greenhouse gases
- Y02C20/40—Capture or disposal of greenhouse gases of CO2
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P60/00—Technologies relating to agriculture, livestock or agroalimentary industries
- Y02P60/20—Reduction of greenhouse gas [GHG] emissions in agriculture, e.g. CO2
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- Chemical & Material Sciences (AREA)
- Engineering & Computer Science (AREA)
- Analytical Chemistry (AREA)
- General Chemical & Material Sciences (AREA)
- Oil, Petroleum & Natural Gas (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Combustion & Propulsion (AREA)
- Mechanical Engineering (AREA)
- General Engineering & Computer Science (AREA)
- Drying Of Gases (AREA)
- External Artificial Organs (AREA)
- Solid-Sorbent Or Filter-Aiding Compositions (AREA)
Description
Technical Field
[0001] The present invention relates to a method for the capture and subsequent storage of CO2 from a CO2 source ranging from sources with extremely low concentrations such as ambient air, via sources with higher concentrations such as air from vegetable storage spaces, to sources with relatively high concentrations such as flue gas from combustion processes. The product contains up to more than 90% CO2, and no use of chemicals in any form ensures safety. Energy consumption is minimized by means disclosed here. More specifically, the present invention relates to the enhancement of a clean adsorption method and process for CO2 capture, by maximization of the adsorbent CO2 storage capacity combined with storage and re-use of heat required in the process, providing energy savings and thus extending the range of useful applications.
Background Art
[0002] An earlier invention, WO2018/034570, presented a system for closed or semi-closed greenhouses. The closing of the greenhouse is accomplished by extracting air at a high rate from the closed greenhouse, dehumidifying it, adjusting the temperature, adding supplementary CO2 captured from the outside air, and subsequently returning this CO2 enriched air to the greenhouse. This stabilizes the greenhouse temperature and humidity and eliminates possibilities for CO2 emissions.
[0003] Plants growing in closed or confined areas such as greenhouses will consume CO2 and thus deplete the CO2 in the air. Therefore most greenhouses have an artificial supply of CO2, such as from a tank with liquid CO2. However, on warm days or with powerful artificial light in the greenhouse, the opening of hatches may be required to reduce the temperature. Air from the greenhouse then flows via the hatches to the outside atmosphere, and added CO2, which is mixed with the greenhouse air, escapes via the hatches along with the escaping air. Up to 75% of added CO2 may be lost as result of this. Therefore, to minimize losses, the CO2 concentration in the air tends to be much lower than the optimum concentration, limiting the CO2 usage and emission to acceptable levels.
Furthermore, air inside greenhouses tends to become very humid as most of the irrigation water is transpired and thus humidifies the air. This also forces the opening of the hatches in many cases.
[0004] Open greenhouses tend to get too high humidity. Plant transpiration in greenhouses increases the relative humidity in the local air. About 90% of the humidity taken up by plants is used for transpiration while 10% is used for growth. The transpiration cools the plant to 2°C or more below the ambient temperature. The rate of transpiration is a function of, among other factors, the radiative heat input and the air relative humidity. High relative humidity, near water vapour saturation in the local air, reduces transpiration. If the temperature then drops, water may precipitate on plant leaves and elsewhere. This increases the risk of fungal diseases. Low relative humidity, such as below 50% in combination with high temperature, may result in excessive transpiration rates. The plant may then start to close the stomata openings, through which transpiration occurs, to reduce transpiration. However, CO2 uptake also occurs through the stomata openings, so this may restrict plant growth. It is important to maintain the local air relative humidity at acceptable if not optimum levels.
[0005] Plant growth rate depends heavily on light including solar radiation or artificial lights. Solar radiation up to at least 600W/m<2 >benefits the plants. Artificial light provides about 250 to 300W/m<2 >and is used whenever the solar radiation is insufficient. However, both sources of light also provide heat and thus affect the greenhouse temperature. The optimum temperature depends on plant species and time of day. Day temperature of 20 to 25°C is suitable for most plants. Optimum night temperatures may be in the range from 15 to 18°C. Typically, the heat input is too high during sunny days and as a result, greenhouse hatches are opened. This helps reduce the temperature and humidity.
[0006] The opening of the hatches also reduces the concentration of CO2 and this may hamper plant growth rate. The depletion may happen very quickly, within minutes. Greenhouses with artificial CO2 addition, such as from liquid CO2 tanks, typically operate with CO2 concentrations in the range from 600 to 800 ppm. With open hatches this drops to about 400 ppm. Up to three quarters of all CO2 artificially injected into the greenhouse is emitted. This is costly and reduces plant growth rates. It limits the economic optimum CO2 concentration in the greenhouse; without such emissions the optimum CO2 concentration might have been much higher such as 1200 ppm.
[0007] The earlier invention, WO2018/034570, solves these issues. Further work with this technology has uncovered new areas where the technology disclosed in can provide great benefits. One example is vegetable storage facilities, where the air tends to become too CO2 rich, such as for example 10000 ppm, caused by slow vegetable degradation. The CO2 capture technology, WO2018/034570, could solve this problem by closing the storage facility and capturing excess CO2. The question if the capture system could capture CO2 from flue gas, typically containing 40000 ppm CO2, has also been raised.
[0008] Among several such other possibilities, the direct capture of CO2 from air, abbreviated DAC (Direct Air Capture) has recently gained significant interest as a means to limit climate change. Such facilities could provide negative emissions, and this could be assigned to positive emissions to annul these.
[0009] Based on the above, there is a need for a CO2 capture system that can capture CO2 from air, from intermediate concentration CO2 sources, and from flue gas without major modifications. The energy consumption should be minimized, the CO2 captured must be available at randomly fluctuating rates, and the CO2 must be clean and suitable for closed spaces where people work.
[0010] CO2 capture systems, from sources where the CO2 is at least partly mixed with components from air and are not pressurized, are usually tailor made to the CO2 source. As an example, CO2 from flue gas is typically captured by adsorption using a reactive amine solution. The main issue with this is amine degradation in the presence of oxygen, forming carcinogenic compounds such as nitrosamines.
[0011] Currently there are no known CO2 capture systems suitable for CO2 sources with intermediate CO2 concentrations such as 10 000 ppm.
[0012] The capture of CO2 from air is under development by some players. One example is the contacting of aqueous potassium hydroxide with air. The hydroxide reacts with CO2 to form potassium carbonate. A major challenge with this is the complexity and energy needed to regenerate the potassium hydroxide solution. Competing adsorption systems, under development to reduce energy requirements, typically use quite complex chemical solutions. Commercializing such systems typically takes a long time. Alternatives include adsorption systems
[0013] WO 2013075981 A3 describes a method for extracting CO2 from air by adsorption on a solid adsorbent. The solid sorbent is functionalized using amine compounds that react with CO2. These chemicals enhance the adsorption capacity and reduce adsorbent sensitivity to humidity. However, during regeneration of the adsorbent, the amine compounds are exposed to hot air with high concentrations of oxygen, causing potential degradation to toxic and possibly carcinogenic products. CO2 from such sources can therefore not be used in the enclosed space of a greenhouse. Performance during long term operation is uncertain, and functionalized solid sorbents may not be commercially available. Among nonfunctionalized adsorbents that are available commercially zeolites, as used in WO2018/034570 are among the most promising
[0014] Zeolites have some very significant advantages. CO2 capture is extremely fast even from dilute sources such as air. Zeolites consist of pure aluminium and silicon oxides. These are inert and safe compounds, much as natural rocks.
Zeolites are commercially available from numerous manufacturers and proven. They are suitable for DAC and also CO2 sources with higher CO2 concentrations than air.
[0015] One disadvantage with zeolites is the affinity for H2O. H2O is preferentially adsorbed. If the zeolite contains more than 2 to 4 weight% H2O, the capacity to adsorb CO2 is reduced. However, if there is moisture in the air or gas containing CO2, this moisture will be adsorbed quickly at the zeolite bed inlet.
Further into the zeolite bed CO2 may still be adsorbed. The overall effect is a slightly reduced capacity to store CO2, while the ability to quickly adsorb CO2 further into the zeolite bed is less affected.
Summary of the Invention
[0016] It is an object of the present invention is to provide a method and an arrangement for efficient capture of CO2, temporarily store the captured CO2 and release the CO2 as nearly 100% CO2 following the adsorption sequence. The invention shall not introduce any new contaminants in the produced CO2 or in the exhaust air. An additional object is to reduce energy consumption, in particular high value energy such as electric or high temperature (above 80 to 100°C) to an absolute minimum. Furthermore, the adsorbent shall be used as efficiently as possible, requiring the least amount for a pre-defined CO2 capture capacity.
Beyond this, the latest commercially available technologies, including air handling which is developing rapidly to reduce energy consumption, shall be utilized to the extent possible. The invention shall have the capability to work with varying CO2 concentrations in the incoming gas, from as low as 50 ppm (which may be desirable in greenhouses during the night) via 400 ppm as in ambient air and 10 000 ppm as in vegetable storage facilities, to 40000 ppm as in flue gas from combustion engines.
[0017] These objects are achieved in a method and arrangement as defined in the claims.
Brief Description of the Drawings
[0018] The invention will now be described in detail in reference to the appended drawings, in which
Figure 1 is a schematic diagram showing one implementation of the invention, with air pre-treatment, CO2 adsorption and energy conservation measures.
Figure 2 is a plot of adsorbent performance when capturing CO2 from air and desorbing at CO2 partial pressure near atmospheric pressure.
Figure 3 is a schematic diagram of adsorbent containment with flow direction and temperature profiles during CO2 adsorption and during adsorbent heating.
Figure 4 is a schematic diagram of CO2 containment with flow direction and temperature profiles during CO2 desorption and during adsorbent cooling.
Figure 5 is a schematic diagram of compact CO2 adsorbent containment systems with adsorbent stacked vertically
Figure 6 is a schematic diagram of heat storage with air or CO2 flow directions during storage of coldness and delivery of heat, and during storage of heat and delivery of coldness.
Figure 7 is a schematic diagram showing one implementation of the invention, with air pre-treatment, dual CO2 adsorption facility and energy conservation measures.
Detailed description of the invention
[0019] In the present description and claims the terms “humidity” and “absolute humidity” are used as a measure of the true water vapour content of air (g/m3). The term “relative humidity” of an air-water vapour mixture is used as a measure of the ratio of the actual partial pressure of water vapour in the air to the partial pressure of water vapour in the air if the air had been saturated at the temperature in question. The term “CO2 concentration” is a measure of the number of molecules of CO2 in the air relative to the total number of gas molecules in the air. It is measured in ppm or parts per million.
[0020] The pressure is herein given in the unit “bara” is “bar absolute”.
Accordingly, 1.013 bara is the normal atmospheric pressure at sea level. In SI units, 1 bar corresponds to 100 kPa.
[0021] The expression “ambient temperature” as used herein may differ with the climate for operation of a closed or semi-closed system served by a process according to the present invention. Normally, the ambient temperature is from about 0 to 40 ºC, but the ambient temperature may also be from sub-zero levels to somewhat higher than 40°C, such as 50 ºC.
[0022] Figure 1 is a principle overall sketch of a system according to a preferred embodiment of the present invention. Part 1 is a process for air cooling and dehumidification and re-heating after CO2 capture, comprising two desiccant wheels and a heat exchanger illustrated as a heat exchange wheel. The desiccant wheels are for air de-humidification. The heat exchange wheel is for air re-heating after CO2 capture, preserving energy. Part 2 is the CO2 capture system with zeolite bed, CO2 desorption gas circulation system, heat storage and CO2 storage.
[0023] Part 1, air cooling and de-humidification with subsequent re-heating, comprises an air inlet conduit 1 where ambient air enters the process driven by a not shown fan. This air may be pre-cooled in a cooler 3 before proceeding to a first desiccant wheel 9. The desiccant wheel comprises a rotating cylinder, typically 10 to 30 cm thick, where the air passes over a water adsorbent such as silica gel. The cylinder has two sections 19 and 8, the first used for air dehydration and the second used for adsorbent regeneration. The sections are shown as 270° for dehydration and 90° for regeneration, but this is for illustration purposes and may vary depending on system design. As an example, 180° for dehydration and 180° for regeneration may also be used. In the section 19 the air gets in contact with or in close proximity to the adsorbent. The adsorbent physically adsorbs humidity according to known equilibria between amount of humidity adsorbed and partial pressure of humidity in the air. Typically, and depending on air temperature and relative humidity, about two thirds of the moisture in the air will be adsorbed in the desiccant wheel 9, section 19. The air pressure drop through the desiccant wheel is very low, in the order of 100Pa. The slow rotation of the wheel, perhaps 10 revolutions per hour, continually moves the humid adsorbent exposed to air from the moisture adsorption section 19 to the regeneration section 8 and after regeneration back to the section 19.
[0024] Downstream the desiccant wheel 9 the air flows in a conduit 20 via a cooler 16 and a conduit 52 to a second desiccant wheel 14. Similar to the desiccant wheel 9 this cylinder may be 10 to 30 cm thick and there is a 270° moisture adsorption section 22 and 90° regeneration or desorption section 13. Silica gel is typically used as desiccant. In the section 22 most of the humidity in the air from the desiccant wheel 9 is removed. The partial pressure of H2O in the air exiting the wheel, conduit 17 leading to the process part 2, shall be such that no water precipitation or ice forms in downstream low temperature processes. Typically this means water dew point in the range -30 to -60°C, preferably about -50°C.
[0025] Dry air returning from the process part 2, conduit 25, is slightly colder than the air going to the process part 2, the conduit 17. This air flows via a small side draw, a conduit 21, typically zero or a few percent of the air in the conduit 25, and then in a conduit 24 to a second side draw, a conduit 5. Air flow in the conduit 5 may be from about one third to two thirds or more of the air in the conduit 25. This dry air flows to a heater 6 where it is heated to typically 50 to 100°C, with preferred temperature in the range 60 to 80°C. After heating, this air flows in a conduit 7 to the regeneration section 13 of desiccant wheel 14. This desorbs water from the H2O adsorbent and thus shifts the equilibrium in the desiccant wheel, section 13, towards lower amounts of H2O in the adsorbent and more humidity in the air. The remaining amount of humidity in the adsorbent is such that, as the adsorbent moves with the rotating wheel into the water adsorption section 22, the adsorbent is capable of reducing the H2O dew point in the conduit 17 to desired values, about -30 to -60°C. Energy for H2O removal in the section 13, essentially vaporization energy for the H2O removed from the adsorbent, is supplied as sensible heat in the air from the heater 6. As H2O is removed from the adsorbent, the air temperature drops by about 25°C and exits the desiccant wheel, a conduit 12, at roughly 35 to 55°C.
[0026] Downstream the desiccant wheel 14 the regeneration air flows in the conduit 12 to a point of mixing with small amounts of extra air from the conduit 21. This reduces the relative humidity of the resulting air mixture, which next flows in a conduit 11 to a heater 10. In the heater 10 the air is trim heated, as required, to desired temperature which, similar to air in the conduit 12, is in the range 35 to 55°C or higher such as 60 to100°C.
[0027] After the trim heating the air flows in a conduit 15 to the adsorbent regeneration section 8 of desiccant wheel 9. In the regeneration section H2O is removed from the desiccant. This shifts the equilibrium in the desiccant wheel, section 13, towards lower amounts of H2O in the adsorbent and more humidity in the air. The shift progresses to a level sufficient for required air dehydration as the desiccant moves with the revolving wheel into the adsorption section 19. Similar to the desiccant wheel 14, the regeneration energy in desiccant wheel 9 is supplied as sensible heat in regeneration air from the conduit 15. The amount of energy required is determined by the vaporization energy of the H2O removed from the adsorbent.
[0028] Moist regeneration air, at a temperature slightly higher than the temperature of the ambient air, is returned to the atmosphere. Excess dry air from the process part 2, a conduit 2, is also returned to the atmosphere or may alternatively be utilized in a not shown vaporization chilling unit for the supply of low temperature coolant to for example coolers 3 or 16.
[0029] Figure 1 part 2 shows a process for the reception of dehydrated air from part 1, cooling of this air, adsorption and desorption of CO2, re-heat of the dehydrated air and return of this air to the process part 1. Air from the conduit 17 is cooled in a heat exchange wheel 18, section 23. The air flows through passages in the wheel and gets in close contact with cold substance, such as a metal, in these openings. This cools the air and at the same time heats the wheel heat storage substance. The wheel rotates slowly, thus moving heated heat storage substance from partition 23 to partition 26 of the wheel, where the wheel heat storage material is re-cooled by cold air from a conduit 33. In this process, the air from the conduit 33 is heated. It exits the heat exchange wheel 18, section 26, in the conduit 25. People skilled in the art will understand that the heat exchange wheel 18 can be replaced by an air – air heat exchanger.
[0030] Cooled air exits the heat exchange wheel 18 in a conduit 28. The temperature is typically in the range -25 to -45°C. Next, the air is trim cooled in a heat exchanger 29 by heat exchange with a coolant provided by a not shown heat pump. After trim cooling, in a conduit 38, the air is about 2 to 5°C colder than in the conduit 28. This air may bypass downstream equipment via a valve 30, enabling the continued operation of the upstream air dehydration and cooling process whenever the downstream CO2 capture process does not need air, such as during CO2 desorption.
[0031] The process downstream of the conduit 38 has four operating modes. These are CO2 adsorption at low temperature in an adsorbent bed 34 located in a container 35, heating of the adsorbent bed, desorption of CO2 from the adsorbent bed and re-cooling of the adsorbent bed before the cycle is repeated.
[0032] During CO2 adsorption cold, dehydrated air flows via a conduit 39, a valve 31 and a conduit 32 to the adsorbent bed 34. Figure 2 shows typical range for low temperature and high adsorbent loading operation, 63, of this operation. The adsorbent bed adsorbs virtually all CO2 from the air. The duration of the adsorption process may be from less than one and up to several hours. Figure 3, part 1, graph 59 shows spatial variation in the air temperature within the adsorbent bed during CO2 adsorption. The temperature is low, in the range from -10 to -50°C, and increases slightly, perhaps by roughly 1°C, from the bed inlet to the bed outlet. The air flow, which is large especially when adsorbing CO2 from lean air as opposed to for example flue gas, flows downwards through the CO2 adsorbent beads. This prevents fluidization of the beads.
[0033] CO2 depleted air from the adsorbent bed 34 is directed via the exit conduit 36 and a valve 37 to the return conduit 33.
[0034] Figure 5, parts 1 and 2 shows compact designs of the adsorbent beds and adsorbent container 35. Air from the conduit 32 flows to two adsorbent beds stacked in a vertical direction, arranged for parallel air flow, such that equal fractions of the total air flows through each bed. An air exit conduit 36 may be on the opposite side of the air inlet flow 32, as shown in Figure 5 part 1, or, for very compact designs, on the same side as shown in part 2. Figure 5 shows two adsorbent beds arranged vertically, but larger numbers of vertically stacked beds such as 3, 4, 5 or more is possible.
[0035] After completion of the first operation mode, CO2 adsorption, the process switches to the second operating mode. The adsorbent bed is heated to the temperature required for CO2 desorption. Figure 2 shows the range 64 of preferred new high temperature and low loading area.
[0036] The heating is accomplished by gas, a mixture of air and CO2, flowing from the warm side 58 of a combined high and low temperature heat storage system 54, 55, 56, 57 and 58. This gas flows via a conduit 53, a conduit 46 and trim heater 41, a conduit 42, the valve 37 and the conduit 36 to the adsorbent bed 34, thus heating the adsorbent bed. The flow direction through the adsorbent bed is the opposite of the direction used during the first operation mode, adsorption.
[0037] When a gas such as air flows through a bed of CO2 adsorbent, comprised of adsorbent beads with diameter typically in the range 4 to 6mm, the heat transfer area between the beads and the air is very large. The heat is therefore transferred rapidly from the air to the beads. This transfer occurs and is completed in a temperature transition zone within the adsorbent bed. Figure 3 part 2 illustrates this. A transition zone 67 receives warm air from below. When the warm air encounters colder adsorbent beads, the beads are warmed and the air is cooled. Thus, at the inlet of the transition zone, the adsorbent beads reach nearly the same temperature as the warm incoming air. In the transition zone the air transfers heat to the beads and is cooled in the process. At the end of the transition zone the air has been cooled to nearly the same temperature as the original low bead temperature, and retains this low temperature as it flows through the remaining adsorbent bed. Figure 3, part 2, graph 61 shows this. Thus, as more heat is supplied with hot incoming air, the transition zone is moving from the adsorbent bed inlet towards the bed outlet, graph 61’. This transition zone movement through the bed may take from minutes up to an hour or more, and the volume of air that has flowed through the adsorbent bed will have been many times larger than the volume of the beads being warmed.
[0038] The key phenomenon is that the adsorbent beads are heated to nearly the temperature of the warm incoming air, thus preserving the valuable high temperature heat of the air. The air going out of the adsorbent bed will be at the low temperature originally in the bed, thus preserving the valuable low temperature heat originally in the adsorbent bed, until the transition zone reaches the end of the bed. It is thus possible to store this coldness for later use. As shown in Figure 6 part 1 this is done in the stacked heat storage beds 54 to 58, located within a container 66. The cold heat transfer gas flows via the conduit 32, the valve 31 now adjusted for the second operating mode, via a fan 43, a conduit 44, through a valve 49 to a conduit 51.
[0039] The stacked heat storage bed receives cold air from the conduit 51. The beds contain metal or ceramic heat storage material with large surface area such as beads with diameters 3 to 10mm. There are several beds, 5 shown in Figures 1 and 6, to minimize heat transport from cold end, near the conduit 51to warm end, near the conduit 53, when heat and coldness are both stored.
[0040] The cold air and CO2 from the conduit 51 flows through bed 54, then to the bed 55 which contains an upwards moving temperature transition zone 65, with temperature profile as shown in graph 69. This transition zone could also be in beds 54, 56, 57 or 58 but not at the top end of the bed 58. This depends on the size of the heat storage and the system operation. People skilled in the art will also understand that the exact shape of the transition zone depends on air flow rate end temperature, heat transfer to and from the heat storage medium and the amount and heat capacity of heat storage medium.
[0041] Air from the transition zone is warm. As the air flows through beds 56, 57 and 58 it stays warm and thus supplies heat to the CO2 adsorbent bed 34 via the conduits 53 and 46, the trim heater 41, the conduit 42, the valve 37 and the conduit 36. The overall effect of this process is to move valuable coldness from the adsorbent bed 34 to the heat storage 66, while at the same time moving heat from the heat storage 66 to the adsorbent bed 34. This continues until the CO2 adsorbent bed is warm and ready for the third operating mode.
[0042] After completion of the second operating mode, CO2 adsorbent heating, the third operating mode, CO2 desorption, starts. Warm air from the adsorbent 34 flows via the conduit 32, in opposite way of the arrow shown in Figure 1, via the valve 31 to the conduit 40. Similar to the second operating mode, valve 31 allows flow from conduit 32 to conduit 40, but is closed to conduit 39. The gas flows from the conduit 40 via the fan 43 and the conduit 44 to the valve 49. This valve is adjusted such the gas can flow to a conduit 45 but not to the conduit 51. Gas from the conduit 45 is directed via conduit 46 to the trim heater 41. Small amounts of heat are provided in the heater 41 to compensate for CO2 desorption heat requirement, typically around 30kJ/mole CO2. In addition any water remaining in air from the adsorbent wheel 14 that has been adsorbed in the adsorbent 34 is removed and requires some extra heat, about 4 kJ/g. The temperature profile within the adsorbent bed 34 during CO2 desorption is indicated in Figure 4, part 1. The temperature is high and nearly constant especially towards the end of the desorption cycle, as shown in graph 60. CO2 desorption proceeds until the temperature is in the range 260 to 300°C as indicated in Figure 2, area 64.
[0043] During operating mode three, when CO2 is desorbed, large volumes of CO2 are supplied from the CO2 adsorbent to the gas phase. In order to keep the system pressure constant, and to preserve the CO2 for later use, the produced CO2 is directed via a conduit 48, a valve 50 and a cooler 65 to CO2 storage 47. This storage may preferably be of the inflatable type.
[0044] People skilled in the art may notice, from Figure 2, that some CO2 may be released from the adsorbent bed 34 during the second operating mode as the adsorbent is heated. This CO2 is also directed to the storage 47.
[0045] After completion of the third operation mode, CO2 desorption, the process switches to the fourth operating mode, adsorbent bed cooling. The adsorbent bed is cooled to the temperature required for CO2 adsorption. This procedure is somewhat similar to the second mode of operation, adsorbent bed heating, but the gas now flows in the opposite direction. The cooling is accomplished by gas, a mixture of air and CO2, flowing from the cold side 54 of the combined high and low temperature heat storage system 54, 55, 56, 57 and 58. This gas flows via the conduit 51, the valve 49, the conduit 44 and the fan 43, via the conduit 40, the valve 31 and the conduit 32 to the adsorbent bed 34. The flow direction through the adsorbent bed is the same as used during the first operation mode, adsorption. Similar to operating mode 2, instead of gradually cooling the whole adsorbent bed the bed will be cooled to nearly the temperature of the incoming cold gas in initially a heat transfer zone near the gas inlet into the bed.
[0046] This temperature transition effect is shown in Figure 4, part 2, graphs 62 and 62’. Graph 62 shows the temperature transition zone at some time into the heating process, graph 61’ at a later time. This transition zone occurs initially at the bed inlet. As cooling progresses, it moves gradually into the bed until it finally reaches the end at the bottom of the bed. As Figure 4 part 2, graph 62 shows, gas from the CO2 adsorbent transition zone is warm, very near the temperature of the adsorption bed before cooling started. This high temperature is preserved for later bed heating by directing the warm gas via the conduit 36, through the valve 37 in a direction to the conduit 42 and the trim heater 41, via conduits 46 and 53, to the warm storage side of heat storage system 54 to 58.
[0047] In a similar manner as in the adsorbent bed 34, this incoming warm air pushes air through the heat storage system. As the air reaches a cold – hot transition zone, shown in Figure 6 part 2, transition zone 65’, it is cooled to nearly the temperature required for the cooling of the adsorbent bed 34. Figure 6 shows the transition zone in heat storage bed 57 but could typically be in the heat storage beds 56 or, towards the end of the adsorbent cooling operation, bed 55 or some distance into bed 54 but not at the end of this bed. Below the transition zone the air is cold. The cold air flows via the conduit 51, the valve 49, the conduit 44, the fan 43, the conduit 40, the valve 31 and the conduit 32 back to the adsorbent bed 34. This moves the transition zone here further into the bed. Completing of the adsorbent bed cooling is accomplished when the air has done many such circulations between the heat storage beds 54 to 58 and adsorbent bed 34 and thus has carried enough coldness from the beds 54 to 58 to the CO2 adsorption bed 34, moving the transition zone to the end of the bed. Simultaneously, all the high temperature heat from CO2 adsorbent bed 34 is transported to the warm end of heat storage units 54 to 58.
[0048] The warm – cold transition zone in the heat storage system has been pushed from the warm end bed 58 towards the cold end bed 54 but not through the cold end bed 54 all the way to the outlet of this unit, the conduit 51. The direction of movement of the warm – cold transition zone is shown in Figure 6 part 2, transition zone 65’ and graph 70.
[0049] After completion of the fourth operating mode, the first operating mode can start, repeating the cycle.
[0050] Figure 7 shows a second embodiment of the invention. A second CO2 adsorption unit 35’ is connected in parallel to the first unit 35. The operation of the second unit is similar to the operation of the unit 35. Operation may be by alternating CO2 adsorption between the two units. For example one of the units, for example the unit 35’, is in the first operating mode, receiving cold and dry air through a conduit 39’, a valve 31’ and a conduit 32’. After adsorption, CO2 and H2O depleted air is routed via a conduit 36’ and a valve 37’ to the conduit 33. During this operation, the other unit, 35, goes through operating modes two, three and four. In this way, the cold and dry air supply may operate continuously and may therefore be smaller in order to supply a specified amount of CO2. In addition, in CO2 adsorbent beds the heat storage may be smaller than would be required according to Figure 1.
Example
[0051] This example will follow the four operating modes. As before, these are CO2 adsorption at low temperature in an adsorbent bed 34 located in a container 35, heating of the adsorbent bed, desorption of CO2 from the adsorbent bed and recooling of the adsorbent bed before the cycle is repeated. The initial state before the CO2 adsorption starts is the same as the state after the completion of the fourth operating mode. The CO2 adsorbent bed has been cooled and high temperature heat is stored in the heat storage 54 to 58. Furthermore, the CO2 adsorbent contains about 15 g residual CO2 per kg CO2 adsorbent from a previous run. The example refers mainly to the Figure 1.
[0052] It is desirable to produce about 600kg CO2 corresponding to 80kg per hour over 7.5 hours. In the first operating mode, CO2 adsorption, 30kg/s ambient air at 15°C, 95% relative humidity and containing 400 ppm CO2, corresponding to 80kg CO2 per hour, is forced through the conduit 1 by a not shown fan. There is no cooling in the cooler 3 and the total H2O flow in this stream is about 1334kg/h. In the desiccant wheel 9 about 854 kg/h H2O is adsorbed and thus removed from the air flow. Air from the desiccant wheel, the conduit 20, now contains about 480kg/h H2O. This corresponds to a water dew point of about 0°C. The adsorption of the H2O in the desiccant wheel is exothermic and the temperature of the air in the conduit 20 is about 33°C. This air is cooled to 15°C in the cooler 16 and then forwarded via the conduit 52 to the desiccant wheel 14, section 22.
[0053] In the desiccant wheel 14 about 477 kg/h H2O is removed from the air. The remaining 3 kg/h flows with the air in the conduit 17. This corresponds to a water dew point of roughly -50°C and the temperature is about 25°C. This air is cooled to -40°C in the heat exchanger wheel 18 and further to -45°C in the trim cooler 29. This trim cooler is operated by a not shown heat pump. Next, the air flows via the valve 31 to the CO2 adsorbent bed 34 where virtually all CO2, 80 kg/h, and virtually all H2O, 3kg/h, are adsorbed. The CO2 and H2O depleted air next flows via the valve 37 and the conduit 33 to the heat exchange wheel 18 where it is heated to about 20°C.
[0054] This air flows in conduits 25 and 24, with no side draw in the conduit 21. One third of the air, about 10 kg/h, flows via the conduit 5 to the heater 6 where it is heated to about 90°C. Subsequently it flows via the conduit 7 to the desiccant wheel 14, regeneration section 13. The air exits the regeneration section 13 in the conduit 12 at a temperature of about 60°C. The H2O flow with the air is about 477kg/h. The air is then re-heated to 90°C in the heater 10 and enters the desiccant wheel 9, regeneration section 8 via the conduit 15. Downstream the regeneration, the conduit 4, the temperature has dropped to about 39°C and the H2O flow with the air is about 1331kg/h.
[0055] The table below shows a summary of the desiccant wheel operation. The stream numbers refer to Figure 1, part 1. Silica gel is used as H2O adsorbent. The objective is to show that in the example, air entering and exiting the desiccant wheel regeneration sections has a lower amount of water adsorbed in the silica gel than the air entering and exiting the adsorption sections. Therefore, the regeneration air will regenerate the desiccant wheel adsorbent by removing water. In this process, the temperature of the air drops from the air inlet to the air outlet. As the table shows, when comparing streams 7 and 17, 12 and 52, 15 and 20 and 4 and 1, the equilibrium amount of H2O adsorbed in the desiccant wheel silica gel is lower into and out of regeneration sections than out of and into, respectively, H2O adsorption sections. People skilled in the art will however notice that the operation of the desiccant wheels is not optimized, especially with respect to the use of heat at the lowest possible temperature for adsorbent regeneration.
[0056] Following operating mode one, operating mode 2 is initiated by adjusting the valve 31 such that there is free flow between the conduits 32 and 40, but no flow into the valve from the conduit 39. Instead, cold air may be bypassed via the valve 30 or the complete cold air supply may be stopped.
[0057] As indicated in Figure 2, the CO2 adsorbent will contain about 80g CO2 per kg adsorbent. After desorption of CO2, with a CO2 partial pressure of 1.0 bar and desorption temperature about 280°C, there will be a residual amount of about 15g CO2 per kg adsorbent. In this example, the net amount of CO2 adsorbed will be 65g per kg CO2. People skilled in the art will understand that with lower partial pressure CO2, such as if diluted by air, or higher desorption temperature such as up to 300°C, the residual amount of CO2 in the adsorbent can be much lower.
[0058] Based on 65g CO2 per kg adsorbent, the adsorption and storage of 600kg CO2, about 9 metric tons of adsorbent is required. 10 metric tons will be assumed in this example, corresponding to about 12.5m<3 >adsorbent beads. Furthermore, the volume of the 30kg/s air flow at -45°C is about 23.5m<3>/s. With superficial air velocity of 0.6m/s the total area of adsorbent becomes roughly 40m<2. >Combined with the adsorbent volume of 12.5m3, the thickness of the adsorbent bed is about 0.31m.
[0059] The heating of 10 metric tons of adsorbent, heat will be supplied from the heat storage 54 to 58, stored in an earlier run, by flowing 30 kg/s gas from the heat storage 58 via the trim heater 41, through the adsorbent bed 34 where the gas gives off heat to the adsorbent and is cooled to the adsorbent temperature of near -45°C such as shown in Figure 3 part 2 graphs 61 and 61’. The cooled gas flows via the fan 43 to the cold end of the heat storage 54 – 58, cooling the cold end and thus preserving the low temperature and pushing more hot gas from the heat storage 58 to the adsorbent bed 34.
[0060] After completion of the CO2 adsorbent heating, the third operating mode CO2 desorption starts. CO2 and air flow out of the CO2 adsorbent 34 via the conduit 32, the valve 31, the conduit 40, the fan 43 which enforces the gas flow and then via the conduits 45 and 46 to the trim heater 41 where heat is supplied for the CO2 and any H2O desorption. The warmed gas then flows via the conduit 42, the valve 37 and the conduit 36 to the adsorbent 34. This continues until the required amount of CO2, 600 kg, is desorbed. The duration of this operation may in the order of one hour depending on the heat input in the heater 41 and the gas circulation rate. Desorbed CO2, about 600 kg, flows via the conduit 48, the valve 50 and the cooler 65 to the CO2 storage 47.
[0061] After completion of the operating mode three, operating mode 4, CO2 adsorbent cooling, starts. This is similar to the operating mode 2, but the air flowing between the heat storage 66 and the CO2 adsorbent unit 35 now flows in the opposite direction, with cold gas flowing from the heat storage via the conduit 51 and downstream equipment to the CO2 adsorbent 34. Here, the gas is heated by remaining heat from the CO2 desorption. This warm gas flows via the conduit 36 to the heat storage 66, heating heat storage beds near the top by pushing a heat transfer zone towards the cold end of the heat storage. Simultaneously, cold gas from the cold end of the heat storage is pushed to the CO2 adsorbent bed 34, further cooling this bed. When the adsorbent bed is cold throughout, the operating mode four is completed and the system is again ready to start with operating mode 1.
[0062] People skilled in the art will notice that the detail design of the air dehydration and cooling before CO2 adsorption is dependent on ambient conditions. A cold environment and therefore low H2O content in the air may result in a much simpler system than shown in Figure 1 part 1, for example one of the desiccant wheels may be omitted.
[0063] People skilled in the art will also notice that much energy can be saved by reducing the mean temperature difference in the heat exchanger wheel 18, and that a normal heat exchanger may be used instead. This reduces the amount of cooling needed in the trim heater 29.
[0064] In addition to this, people skilled in the art will understand that instead of zeolite adsorption beds for CO2 and H2O, potentially more efficient and less H2O sensitive CO2 adsorption systems such as amine functionalized alumina may be used, but this may introduce the disadvantage of potential degradation of chemicals and production of toxic substances.
[0065] Furthermore it will be understood that while the dehydration and cooling of the air may seem equipment and energy intensive, the current emphasis on low emission has forced and is forcing the development of extremely efficient air dehydration and cooling systems. The desiccant wheel is an example. Such systems have been and will continue to be adapted in order to simplify the air pretreatment.
Claims (12)
1. A method for capturing CO2 from a CO2 source, such as ambient air or flue gases, including the steps of:
a) conducting a stream of said air/gases through a bed (34) of CO2 adsorbent material capturing CO2 from the streamed air/gas in the CO2 adsorbent bed,
b) conducting a stream of heating gas through a heat storage and recovery unit (66) and said CO2 adsorbent bed (34) transferring stored heat from said heat recovery unit to said CO2 adsorbent bed, said heat storage and recovery unit (66) containing metal or ceramic heat storage material,
c) circulating said heating gas through the CO2 adsorbent bed in a closed loop desorbing CO2 from the CO2 adsorbent bed,
d) extracting the desorbed CO2,
e) conducting a stream of cooling gas through the heat storage and recovery unit and the CO2 adsorbent bed transferring heat from the CO2 adsorbent bed to the heat recovery unit.
2. A method according to claim 1, wherein in step a) the stream of said air/gases is conducted through the bed (34) of CO2 adsorbent material in a first direction, in step b) the stream of heating gas is conducted through the heat storage and recovery unit (66) and said CO2 adsorbent bed (34) in a second direction opposite said first direction, and in step e) the stream of cooling gas is conducted through the heat storage and recovery unit and the CO2 adsorbent bed in the first direction.
3. A method according to claim 1 or 2, wherein the stream of ambient air or flue gases is dried and cooled before being conducted to the CO2 adsorbent bed.
4. A method according to claim 3, wherein the gases are conducted through a first desiccant wheel (9) and then through a heat exchanger (18) before being conducted to the CO2 adsorbent bed, and gas output from the CO2 adsorbent bed is returned through the heat exchanger and first desiccant wheel.
5. A method according to claim 3, wherein the gases are conducted through a first desiccant wheel (9) and then through second desiccant wheel (14) and a heat exchanger (18) before being conducted to the CO2 adsorbent bed, and gas output from the CO2 adsorbent bed is returned through the heat exchanger, first desiccant wheel and second desiccant wheel.
6. An arrangement for capturing CO2 from a CO2 source, such as ambient air or flue gases, the arrangement including:
a CO2 capture container (35) with a CO2 adsorbent bed (34) adapted to adsorb CO2 during an adsorption step and desorb CO2 during a desorption step,
c h a r a c t e r i z e d i n that the arrangement further includes a heat storage and recovery unit (66) adapted to transfer stored heat to the CO2 adsorbent bed prior to the desorption step and recover heat from the CO2 adsorbent bed after the desorption step, the heat storage and recovery unit (66) containing metal or ceramic heat storage material.
7. An arrangement according to claim 6, wherein an inlet conduit (39) is connected to a first port of a first three-way valve (31), an input line (32) of the CO2 capture container (35) is connected to a second port of the first valve (31), an output line (36) of said container (35) is connected to a first port of a second threeway valve (37), a second port of said second three-way valve (37) is connected to an outlet conduit (33), a third port of said first three-way valve (31) is connected to a first port of a third three-way valve (49), a second port of the third three-way valve (49) is connected to a first port of the heat recovery unit (66), a second port of the heat recovery unit (66) is connected to a third port of the second three-way valve (37), a bypass conduit (45) is connecting a third port of the third three-way valve (49) to the second port of the heat recovery unit (66), the arrangement further including a circulation pump (43) installed either at the third port of the first three-way valve (31) or at the third port of the second three-way valve (37), and a CO2 outlet conduit (48) with an outlet valve (50).
8. An arrangement according to claim 6 or 7, wherein the CO2 adsorbent bed (34) includes zeolite material.
9. An arrangement according to claim 6 to 8, wherein the heat recovery unit (66) includes several beds (54, 55, 56, 57, 58) of a heat storage medium.
10. An arrangement according to claim 9, wherein the heat storage medium contains beads of a metallic or ceramic heat storage material with large surface area.
11. An arrangement according to claim 7 to 10, wherein a gas intake conduit (1) is connected to a drying input of a first desiccant wheel (9), the drying output of which is connected to a first side input of a heat exchanger (18), the first side output of which is connected to said inlet conduit (39), the outlet conduit (33) is connected to a second side input of the heat exchanger (18), the second side output of the heat exchanger (18) is connected to a gas outlet line (25, 24, 2), and wherein a recovery input of said first desiccant wheel (9) is connected to gas outlet lines 24,25.
12. An arrangement according to claim 11, wherein a second desiccant wheel (14) is installed between the first desiccant wheel (9) and the heat exchanger (18).
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NO20200431A NO346496B1 (en) | 2020-04-07 | 2020-04-07 | A method and arrangement for capturing CO2 |
US17/917,536 US20230137348A1 (en) | 2020-04-07 | 2021-04-07 | A method and arrangement for capturing CO2 |
CA3173632A CA3173632A1 (en) | 2020-04-07 | 2021-04-07 | A method and arrangement for capturing carbon dioxide from a gas stream using an adsorption system comprising a heat storage and recovery unit |
PCT/NO2021/050095 WO2021206564A1 (en) | 2020-04-07 | 2021-04-07 | A method and arrangement for capturing carbon dioxide from a gas stream using an adsorption system comprising a heat storage and recovery unit |
EP21723437.6A EP4132685B1 (en) | 2020-04-07 | 2021-04-07 | A method and arrangement for capturing carbon dioxide from a gas stream using an adsorption system comprising a heat storage and recovery unit |
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EP4166215A1 (en) * | 2021-10-12 | 2023-04-19 | TotalEnergies OneTech | A carbon dioxide removal installation and associated method |
DE102021130001A1 (en) * | 2021-11-17 | 2023-05-17 | Audi Aktiengesellschaft | Utilization of carbon dioxide from the ambient air |
DE102021130002A1 (en) | 2021-11-17 | 2023-05-17 | Audi Aktiengesellschaft | Utilization of carbon dioxide from the ambient air |
CN114294039B (en) * | 2021-12-14 | 2023-12-22 | 天地科技股份有限公司 | Reactive power carbon dioxide multipath recovery device in coal mine air shaft |
CN114588754B (en) * | 2022-03-02 | 2023-04-21 | 百年控股(深圳)有限公司 | Device and method for capturing and compressing carbon dioxide in air |
WO2023191638A1 (en) * | 2022-03-31 | 2023-10-05 | Greencap Solutions As | Sorbent unit, and system and method for purification of gas |
CN115414765B (en) * | 2022-09-22 | 2024-01-23 | 江苏科技大学 | Carbon dioxide trapping system with reflux circulation function and trapping method thereof |
NO20221044A1 (en) * | 2022-09-30 | 2024-04-01 | Greencap Solutions As | A method and system for removing CO2 from a gas |
NO20221113A1 (en) * | 2022-10-18 | 2024-04-19 | Greencap Solutions As | Method and system for direct air capture of CO2 utilizing a physical adsorbent |
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US20120204717A1 (en) * | 2011-02-11 | 2012-08-16 | Munters Corporation | Apparatus and method for removing co2 from a production plant discharge |
WO2018034570A1 (en) * | 2016-08-16 | 2018-02-22 | Greencap Solutions As | A system for climate control in closed or semi closed spaces |
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US4536197A (en) * | 1983-09-16 | 1985-08-20 | Cook Thomas E | Process and apparatus for removing adsorbed material from an adsorber |
JPH09122432A (en) * | 1995-11-01 | 1997-05-13 | Mitsubishi Heavy Ind Ltd | Gas separator using pressure swing adsorption process |
EP2782657B1 (en) | 2011-11-25 | 2016-12-28 | Climeworks AG | Distributed building-integrated carbon dioxide extraction system reducing fresh air requirements |
AU2019284807A1 (en) * | 2018-06-14 | 2020-10-15 | Climeworks Ag | Method and device for adsorption/desorption of carbon dioxide from gas streams with heat recovery unit |
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US20120204717A1 (en) * | 2011-02-11 | 2012-08-16 | Munters Corporation | Apparatus and method for removing co2 from a production plant discharge |
WO2018034570A1 (en) * | 2016-08-16 | 2018-02-22 | Greencap Solutions As | A system for climate control in closed or semi closed spaces |
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WO2021206564A1 (en) | 2021-10-14 |
EP4132685A1 (en) | 2023-02-15 |
NO20200431A1 (en) | 2021-10-08 |
US20230137348A1 (en) | 2023-05-04 |
CA3173632A1 (en) | 2021-10-14 |
EP4132685B1 (en) | 2024-05-15 |
EP4132685C0 (en) | 2024-05-15 |
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